Humulus lupulus L. Strobilus Photosynthetic Capacity and Carbon Assimilation

The economic value of Humulus lupulus L. (hop) is recognized, but the primary metabolism of the hop strobilus has not been quantified in response to elevated CO2. The photosynthetic contribution of hop strobili to reproductive effort may be important for growth and crop yield. This component could be useful in hop breeding for enhanced performance in response to environmental signals. The objective of this study was to assess strobilus gas exchange, specifically the response to CO2 and light. Hop strobili were measured under controlled environment conditions to assess the organ’s contribution to carbon assimilation and lupulin gland filling during the maturation phase. Leaf defoliation and bract photosynthetic inhibition were deployed to investigate the glandular trichome lupulin carbon source. Strobilus-level physiological response parameters were extrapolated to estimate strobilus-specific carbon budgets under current and future atmospheric CO2 conditions. Under ambient atmospheric CO2, the strobilus carbon balance was 92% autonomous. Estimated strobilus carbon uptake increased by 21% from 415 to 600 µmol mol−1 CO2, 14% from 600 to 900 µmol mol−1, and another 8%, 4%, and 3% from 900 to 1200, 1500, and 1800 µmol mol−1, respectively. We show that photosynthetically active bracts are a major source of carbon assimilation and that leaf defoliation had no effect on lupulin production or strobilus photosynthesis, whereas individual bract photosynthesis was linked to lupulin production. In conclusion, hop strobili can self-generate enough carbon assimilation under elevated CO2 conditions to function autonomously, and strobilus bracts are the primary carbon source for lupulin biosynthesis.


Introduction
The atmospheric CO 2 concentration is predicted to rise to approximately 500 ppm, reaching 600 ppm and 700 ppm by 2060 and 2075 [1] (pp. 673-816). Elevated atmospheric CO 2 concentrations can increase a plant's photosynthesis rate. Most studies of the mechanisms by which plants respond to environmental conditions, such as elevated atmospheric CO 2 , focus on leaves and overlook other green plant organs [2]. It has been shown that extra photosynthetic plant organs, such as the bracts found in abundance in Humulus lupulus L. (hop), are a source of assimilated carbon on the ecological and agricultural scales [2][3][4][5][6].
Like leaves, bracts contain chlorophyll and share similarities with leaf morphology and anatomy. However, bract surface area on the plant scale is frequently negligible in comparison to leaves. Hops are an exception, producing upwards of 80 superimposing bracts per strobilus, typically called a hop cone, during the generative growth phase. Each bract on the strobilus is accompanied by two adjacent considerably smaller bracteoles (secondary bracts) [7,8]. The hop bracts and bracteoles' primary function is to subtend a small flower and glandular trichomes (micro-organs), which are concentrated at the base of each bract. Hop anatomical features are illustrated in Neve [7]. Although a few glandular trichomes exist elsewhere on hop vegetation (e.g., leaves), the bract contains the vast majority. The preponderance of glandular trichomes on bracts indicates that bracts could contribute a significant amount of carbon to their development, analogous to the bracts on cotton bolls [6]. 2 of 13 To date, a literature survey reveals a single study on hop strobilus carbon assimilation [9]. Fifty years ago, ambient CO 2 concentrations were approximately 28% lower, at 325 ppm vs. 416 ppm [1]. Consequently, the extent to which hop bract and bracteole photosynthetic activity responds to current and/or elevated atmospheric CO 2 is not known. It may be that the strobilus can function autonomously regarding carbon accumulation, where bracts play a significant role in supplying carbohydrate to hop glandular trichomes, commonly known as 'lupulin glands'. Studies designed to investigate this possibility have not been conducted.
Hop bracts can photosynthesize, and stomata exist on both the adaxial and abaxial surface [9]. The bract surface resembles leaf stoma distribution [10], though approximately 95% fewer stoma exist per surface area in two-sided amphistomatic bract anatomy as compared to on hypostomatic hop leaves [9]. Regardless, the hop bracts that comprise the strobilus contain everything that is of value to beer, predominantly lupulin gland resins, simply termed lupulin. Lupulin consists of a combination of essential oils and alpha and beta acids, which constitute the flavor and fragrance ingredients in beer. The lupulin accumulates during the strobilus maturation stage of the hop fruiting cycle. During this phase, hop strobili amass approximately half of the total aboveground dry matter [7,8]. Strobilus carbon assimilation, crucial to lupulin biosynthesis for beer production, thus warrants further investigation.
Understanding hop strobilus responses to CO 2 and light would provide insight into their carbon assimilation, autonomy, and response to future and controlled-environment CO 2 and light conditions. In the present study, we focused on strobilus carbon exchange responses to CO 2 and light, two growth variables that change spatially and temporally. We hypothesized that under enriched CO 2 and supplemental light conditions, strobilus function autonomously with respect to carbon assimilation. Simultaneously, we tested a second hypothesis that bracts autonomously generate carbohydrates for lupulin biosynthesis. By isolating individual bract lupulin gland development, bract-generated carbon for lupulin was separated from leaf-derived.

Strobilus Gas Exchange
Net Photosynthesis Versus CO 2 and Photosynthetically Active Radiation Replicate strobilus net photosynthesis (A n ) values per intercellular CO 2 (C i ) concentration and photosynthetically active radiation (PAR) levels were not different between the four measurement intervals (two-tailed t-tests; p > 0.16-0.8 and p > 0.23-0.84). Maximum Rubisco carboxylation rate (V cmax ) and light compensation point (L c ) values were also stable across the four collection intervals. Figure 1 shows the increase in A n , with increases in estimated C i for hop strobili. C i estimates above 1500 µmol mol −1 showed increases in A n variation. Nonetheless, strobilus CO 2 saturation was still not achieved at 1900 ppm atmospheric CO 2 ( Figure 1). Carboxylation limited by the regeneration of inorganic phosphate requires a good estimate of the potential electron transport rate. Due to a lack of CO 2 saturation in our A n /C i response curves, we do not report electron transport (A nj ) or inorganic phosphate supply (A np ).
Compared to leaves, strobilus light saturation (L s ) occurred at 341 as opposed to 612 µmol m −2 s −1 (Table 1) [11]. It is probable that high light intensity reduces bract V cmax in hop strobili. In our measurements, PAR above 600 µmol photons m −2 s −1 reduced A n ( Figure 2). Although we avoided this phenomenon by exposing strobili to light saturation at PAR below 600 µmol m −2 s −1 during the construction of our A n /C i curves, supraoptimal light effects could take place in outdoor conditions. For example, 500 µmol m −2 s −1 PAR represents approximately 25% of the sun intensity on the Earth's surface. We discovered that approximately 400 µmol m −2 s −1 PAR is sufficient to achieve strobilus L s and that levels higher that 600 µmol m −2 s −1 PAR can decrease A n ( Figure 2).
Compared to leaves, strobilus light saturation (Ls) occurred at 341 as opposed to 6 µmol m −2 s −1 (Table 1) [11]. It is probable that high light intensity reduces bract Vcmax in h strobili. In our measurements, PAR above 600 µmol photons m −2 s −1 reduced An (Figure Although we avoided this phenomenon by exposing strobili to light saturation at PA below 600 µmol m −2 s −1 during the construction of our An/Ci curves, supraoptimal lig effects could take place in outdoor conditions. For example, 500 µmol m −2 s −1 PAR rep sents approximately 25% of the sun intensity on the Earth's surface. We discovered th approximately 400 µmol m −2 s −1 PAR is sufficient to achieve strobilus Ls and that lev higher that 600 µmol m −2 s −1 PAR can decrease An ( Figure 2).  We observed a strobilus Lc approximately three times higher than that of leaves (76.7 vs. 26 µmol m −2 s −1 PAR) ( Table 1) [11]. Light-saturated photosynthetic rate at ambient atmospheric CO2 (415 µmol mol −1 ) (Amax), on the other hand, was approximately four times lower in strobilus bracts under current ambient CO2 concentrations as compared to leaves Figure 2. The net photosynthesis of hop strobili as a function of photosynthetically active radiation (PAR). Cuvette O 2 was atmospheric ambient (~21%). Strobilus temperature was controlled at 25 • C and CO 2 at approximately atmospheric ambient (415 µmol mol −1 ). Samples were pooled across four measurement intervals (means ± SE). Table 1. Photosynthetic response parameters for hop strobili of cv. 'Centennial' measured at 25 • C. Means ± standard error (SE). Photosynthetically active radiation response parameters are lightsaturated photosynthetic rate at 415 µmol mol −1 CO 2 (A max , µmol m −2 s −1 ), dark respiration rate (R d , µmol m −2 s −1 ), quantum yield (φ, mol C mol −1 ), and light saturation point (L s , µmol m −2 s −1 ) at 415 µmol mol −1 and 25 • C. CO 2 response parameters are maximum Rubisco carboxylation rate (V cmax ) (µmol m −2 s −1 ) and CO 2 compensation point (Γ, µmol mol −1 ) at 25 • C. Samples were pooled across four measurement intervals. Number of strobili n = 24.

Parameter
Mean ± SE We observed a strobilus L c approximately three times higher than that of leaves (76.7 vs. 26 µmol m −2 s −1 PAR) ( Table 1) [11]. Light-saturated photosynthetic rate at ambient atmospheric CO 2 (415 µmol mol −1 ) (A max ), on the other hand, was approximately four times lower in strobilus bracts under current ambient CO 2 concentrations as compared to leaves (4.2 vs. 17.3 µmol m −2 s −1 ) ( Table 1) [11]. Likewise, strobilus mean quantum yield (φ) was half that observed in leaves of the same cultivar (Table 1) [11]. Dark respiration (R d ) was slightly higher in strobilus as compared to leaf tissue (−2.1 vs. −1.7 µmol m −2 s −1 ) ( Table 1) [11]. The CO 2 compensation point (Γ) was higher than values generally observed in C 3 leaves (Table 1) [11]. Figure 3 illustrates summed 30 min diurnal strobilus carbon estimates of net daily carbon per strobilus surface area, as described in Section 4.6. Apart from our strobilus gas exchange measurements not encompassing the earliest growth stage, we discovered that strobili exposed to 2022 Yakima, WA, weather variables maintain a close to autonomous carbon balance over the course of 30 days prior to harvest (e.g., Figure 3). On average, strobili generated 92% of their own carbon over the course of 30 days prior to harvest. The daily carbon uptake of strobili exposed to Yakima, WA, 2022 weather conditions at atmospheric CO 2 of 600 µmol mol −1 increased (Figure 3). At 600 µmol mol −1 , strobili generated 113% of their net carbon balance. Likewise, carbon uptake increased at atmospheric CO 2 of 900, 1200, 1500, and 1800 µmol mol −1 ( Figure 3). This resulted in a positive carbon balance of 128%, 136%, 140%, and 143% of net strobilus carbon supply, respectively.

Leaf Defoliation and Bract Carbon Assimilation Interruption
To test whether lupulin metabolite production in hops can be explained by a specific photosynthetic source, we removed all the hop leaves after the plants transitioned into reproduction and separately blocked bract photosynthesis from accepting electrons from

Leaf Defoliation and Bract Carbon Assimilation Interruption
To test whether lupulin metabolite production in hops can be explained by a specific photosynthetic source, we removed all the hop leaves after the plants transitioned into reproduction and separately blocked bract photosynthesis from accepting electrons from photosystem I (PSI) via herbicide application. Defoliation did not affect strobilus photosynthetic activity or lupulin production. Blocking bract photosynthesis, to isolate the bract as the sole remaining photosynthetic organ within the strobilus, did prevent lupulin glands from filling. Lupulin glands were amassed approximately equally at the base of each bract in both treatments. Bracts that were not treated yet resided on the same strobilus as some with herbicide treatment filled their basal lupulin glands normally with no visual signs of chlorophyll degradation. Herbicide-treated bracts, however, visually expressed tissue mortality at the site of herbicide contact and failed to fill their lupulin glands ( Figure 4). We note that the base of each bract was purposefully not treated with herbicide so as not to injure lupulin glands. Although lupulin glands were present in equal numbers on treated and untreated bracts, glands on bracts treated with herbicide did not fill with lupulin, whereas the glands on untreated bracts of the same strobilus filled ( Figure 5). Our results indicate that there is a link between bract photosynthetic electron transport and lupulin biosynthesis, providing indirect support that the bract organ is the primary carbohydrate source of lupulin ( Figure 5).

Leaf Defoliation and Bract Carbon Assimilation Interruption
To test whether lupulin metabolite production in hops can be explained by a photosynthetic source, we removed all the hop leaves after the plants transitio reproduction and separately blocked bract photosynthesis from accepting electro photosystem I (PSI) via herbicide application. Defoliation did not affect strobilu synthetic activity or lupulin production. Blocking bract photosynthesis, to isolate t as the sole remaining photosynthetic organ within the strobilus, did prevent glands from filling. Lupulin glands were amassed approximately equally at the each bract in both treatments. Bracts that were not treated yet resided on the sam lus as some with herbicide treatment filled their basal lupulin glands normally visual signs of chlorophyll degradation. Herbicide-treated bracts, however, visu pressed tissue mortality at the site of herbicide contact and failed to fill their glands ( Figure 4). We note that the base of each bract was purposefully not trea herbicide so as not to injure lupulin glands. Although lupulin glands were pr equal numbers on treated and untreated bracts, glands on bracts treated with h did not fill with lupulin, whereas the glands on untreated bracts of the same s filled ( Figure 5). Our results indicate that there is a link between bract photosynth tron transport and lupulin biosynthesis, providing indirect support that the bract the primary carbohydrate source of lupulin ( Figure 5).  Plants 2021, 10, x FOR PEER REVIEW 6 control. Treated and control bracts on the strobili above the bracts illustrate the random indiv treatment of bracts within a strobilus.

Discussion
Architecturally and geometrically, the hop strobilus arranges the bract leaf-lik gans around a cylindrical axis. The arrangement is one of the most compact that ca achieved when positioning lateral leaf-like organs around a cylindric axis. This con ration not only wholly exposes the strobilus surface area to environmental resources, as light, but it also allows for two strobilus photosynthesis CO2 sources: external at pheric CO2 and internal CO2 released from organ respiration. Aschan and Pfanz [12] s that effective internal re-fixation of CO2 released from respiratory reactions supplem external atmospheric CO2 in extra photosynthetic plant organs [12]. Hop strobili are l no exception due to the presence of stomata on both the bract adaxial and abaxial sid Respiratory CO2 released within the strobilus would result in enrichment above amb atmospheric conditions, resulting in a shift in the atmospheric CO2 to O2 ratio, w would reduce the O2 inhibition of carboxylation and photorespiration [13,14]. Altho bracts possess fewer stomata per unit area compared to leaves [9], their thickness is stantially less than that of leaves. In fact, hop bracts are moist photosynthetic semi-tr lucent leaf-like structures ( Figure 5). CO2 is very soluble in water and can quickly di through moist permeable membranes. For example, as compared to other gases with nificantly lower molecular weight (e.g., helium or hydrogen) CO2′s high solubility in w allows it to diffuse faster through moist membranes.
The net photosynthetic contribution of green reproductive organs to their ca budget depends on ambient environmental conditions. However, substantial amoun their carbon requirement can be fixed in situ [15,16]. On a chlorophyll basis, studie green plant reproductive structures have shown a 1-3 times higher photosynthetic as ilatory capacity as compared to leaves of the same plant species [17][18][19][20][21]. However photosynthetic rates and stomatal densities of reproductive organs tend to be lower those of leaves [2]. In 1970, with ambient atmospheric CO2 concentrations of app mately 325 ppm, Peat and Thomas [9] found hop cones ≥ 16 days of age to be capab

Discussion
Architecturally and geometrically, the hop strobilus arranges the bract leaf-like organs around a cylindrical axis. The arrangement is one of the most compact that can be achieved when positioning lateral leaf-like organs around a cylindric axis. This configuration not only wholly exposes the strobilus surface area to environmental resources, such as light, but it also allows for two strobilus photosynthesis CO 2 sources: external atmospheric CO 2 and internal CO 2 released from organ respiration. Aschan and Pfanz [12] show that effective internal re-fixation of CO 2 released from respiratory reactions supplements external atmospheric CO 2 in extra photosynthetic plant organs [12]. Hop strobili are likely no exception due to the presence of stomata on both the bract adaxial and abaxial side [9]. Respiratory CO 2 released within the strobilus would result in enrichment above ambient atmospheric conditions, resulting in a shift in the atmospheric CO 2 to O 2 ratio, which would reduce the O 2 inhibition of carboxylation and photorespiration [13,14]. Although bracts possess fewer stomata per unit area compared to leaves [9], their thickness is substantially less than that of leaves. In fact, hop bracts are moist photosynthetic semi-translucent leaf-like structures ( Figure 5). CO 2 is very soluble in water and can quickly diffuse through moist permeable membranes. For example, as compared to other gases with significantly lower molecular weight (e.g., helium or hydrogen) CO 2 's high solubility in water allows it to diffuse faster through moist membranes.
The net photosynthetic contribution of green reproductive organs to their carbon budget depends on ambient environmental conditions. However, substantial amounts of their carbon requirement can be fixed in situ [15,16]. On a chlorophyll basis, studies on green plant reproductive structures have shown a 1-3 times higher photosynthetic assimilatory capacity as compared to leaves of the same plant species [17][18][19][20][21]. However, the photosynthetic rates and stomatal densities of reproductive organs tend to be lower than those of leaves [2]. In 1970, with ambient atmospheric CO 2 concentrations of approximately 325 ppm, Peat and Thomas [9] found hop cones ≥ 16 days of age to be capable of partly replacing respiratory losses. Measuring similarly aged strobilus, our A n results match the findings of Peat and Thomas [9]. Measured at current ambient atmospheric concentrations (415 µmol mol −1 CO 2 ), we found strobili to be capable of counterbalancing 92% of respiratory loss over the course of the month prior to strobilus harvest. When exposed to elevated CO 2 concentrations, the strobilus carbon budget became positive, thus indicating a strong photosynthetic sugar-producing role in the later stage of the hop strobilus. Similar to prior studies on other reproductive structures, we found that the carbon cost in terms of a strobilus carbon balance may be fully compensated for by increasing photosynthetic rates of the reproductive structure [2,22,23]. Though leaves cannot be ruled out as a carbon source for strobilus development at the onset of the reproductive stage, leaves showed clear signs of senescence during the strobilus generative phase, whereas strobilus photosynthetic capacity did not decline during the hop flowering phase [24]. This indicates that under optimal environmental conditions, strobili can function autonomously with respect to carbon assimilation in the latter phase of the hop growing cycle.
Reproductive structure photosynthesis is common and can provide a source of assimilated carbon on the ecological and agricultural scales [2][3][4][5][6]25]. Under certain environmental conditions, we found strobilus photosynthesis to be capable of counterbalancing respiratory loss, which would decrease the carbon cost of the reproductive structure to the remaining portion of the plant. Moreover, the photosynthesis derived from the strobilus can generate significant amounts of photoassimilates, akin to the large body of evidence for other reproductive organs [2,12]. The hop strobilus is developed in the late stage of the growth cycle. Therefore, its younger photosynthetic machinery can remain photosynthetically active when older leaves have started to senesce (e.g., [26]). Compared to leaves, strobilus PAR L s was >100 µmol m −2 s −1 lower, whereas the L c was approximately two times higher [11]. Leaf and strobilus respiration rates were similar, but strobilus V cmax decreased by approximately 71% and Γ increased by 43% [11]. Nonetheless, generating a source of carbon from photosynthesis when other source tissue, such as leaves, are senescing allows the strobili to positively contribute to the carbon requirement of reproduction.
Generative-phase defoliated versus leaf-intact plants showed no indication of an influence on trichome gland filling. This suggests that the bracts on strobili can compensate for the loss of sugars from leaves. In contrast, individual bract carbon assimilation interruption versus non-interruption had a clear influence on trichome gland filling. It was proposed that lupulin glands primarily synthesize hop bitter acids [27][28][29]. Due to glandular trichome lupulin accumulation in control bracts and the lack thereof in photosynthetically inhibited bracts, it appears that lupulin biosynthesis may be primarily dependent on bract as opposed to leaf carbon supply. This indicates that glandular trichome lupulin biosynthesis is linked to bract carbon assimilation. It may be that during the generative phase, the hop bine and laterals take on a fundamentally different purpose, mostly functioning as structural support and a pathway for water and nutrient transport [2,30]. In so doing, bine and lateral vegetative structures in the later strobilus development stages would primarily function to spatially disperse strobili throughout the crown to minimize their environmental resource competition, such as light foraging.
The consolidation of carbon-generating and reproductive parts within a strobilus inflorescence may optimize carbon partitioning. In addition, fewer stomata are required due to the higher level of carbon re-fixation from respiratory CO 2 permeating the bract membrane. In this situation, a reduction in stomatal densities can increase water-use efficiency without a substantial reduction in photosynthetic capacity [31]. Given that hop bracts contain the majority of hop glandular trichomes, it would make sense that bracts provide a portion, if not all, of the carbon to biosynthesize lupulin. In fact, active sinks, such as trichomes, are generally fed by the nearest carbon source [32]. We found that the bract-intensive strobilus possessed a strong capacity to photosynthesize, and provided significant assimilatory products to lupulin under enriched CO 2 conditions. In addition, strobili bracts showed a lower light saturation as compared to leaves [11]. Future research should investigate strobili chlorophyll fluorescence responses to PAR to possibly explain the observation that supraoptimal PAR lowered A n .
In summary, we assessed the link between individual bract photosynthesis and lupulin biosynthesis. The results show unequivocally that the photosynthetic activity of the hop strobilus can maintain a high proportion of the hop plant's fitness in the later generative phase of the hop. As atmospheric CO 2 concentrations rise, autonomy of hop strobili could progress further, and one would expect moderate elevations in external CO 2 concentrations to increase the strobilus carbon supply. However, the carbon gains may be offset by elevated respiration in the face of rising atmospheric temperatures. Nonetheless, our gas exchange results indicate that under current ambient CO 2 conditions, mature hop strobili can function close to carbon autonomy in the early fall (August) weather of Yakima, WA [33]. Diurnally, the strobilus assimilation gain during daylight nearly counterbalanced the respiratory CO 2 release in the dark at current ambient CO 2 concentrations. At CO 2 concentrations above ambient, the data presented show that ripening hop strobili are capable of a significantly higher proportion of carbohydrate generation.

Plant Material
Research experiments were conducted at the Colorado State University (CSU) Horticulture Center in Fort Collins, Colorado. Over the course of the study, female tissue culture-propagated plantlets were used (Summit Plant Labs Inc., Fort Collins, CO, USA). The public variety 'Centennial' was selected due to the representative genetic hop parentage (Brewers Gold + Fuggle + East Kent Golding + Bavarian) [34]. Centennial is 'ripe to flower' when ≥ 20 nodes are visible [7,35].
Plantlets were transplanted into 11 L bato buckets containing 100% horticulture-grade perlite. Plant spacing, irrigation, fertilization, and cultural growing condition procedures are outlined in Bauerle [36]. One bine per container was trained to a vertical net trellis at approximately 0.5 m bine length. We note that although there is not a 'standard' bine spacing per unit area for hops, the plant density in this study equated to 10,764 bines per ha −1 , which is a plant density similar to manual field hop production [8]. Initially, all pots were watered to saturation and permitted to drain for 18 h. Thereafter, container moisture capacity was maintained daily. White plastic sheeting was cut and placed on the substrate surface to eliminate evaporation.

Environmental Conditions
Top lights and interlighting bars (suspended horizontally at 150 and 210 cm) (Green-Power LED ® , Philips Lighting, Amsterdam, The Netherlands) provided supplemental photosynthetically active radiation (PAR) per plant row (100-700 umol m −2 s −1 during photoperiod). Day length was controlled at 18 and 15 h during the vegetative and generative phases. Controllers were programmed to permit the maximum amount of light penetration (shade cloth was only pulled when intense solar radiation and temperatures demanded additional cooling efforts), and daytime ambient PAR at the canopy surface was generally 800-1100 µmol m −2 s −1 . Greenhouse conditions were programmed to a set point air temperature of 26 • C during the photoperiod and 20 • C during the dark period with a 45 min temperature step change between the two. Daytime temperatures over the experimental period averaged 26.4 • C, but in some instances, temperatures climbed higher despite continuous cooling. Supplemental humidity was provided via an evaporative cooling pad and the daytime saturation vapor pressure deficit (VPD) averaged 1.9 kPa. Air temperature and relative humidity (RH; %) were measured using EHT RH/temperature sensors mounted at the top of the canopy (Meter Devices, Pullman, WA, USA) and PAR using two quantum line sensors placed parallel to the north/south row orientation adjacent to the plant stems (model LI191R, Li-Cor Inc., Lincoln, NE, USA). A third quantum line sensor was placed 0.5 m above the canopy. The line sensors sampled PAR every minute and then recorded a 15 min average (CR10x; Campbell Scientific, Logan, UT, USA).

Strobilus Gas Exchange and Light Absorption Measurements
To examine the photosynthetic capacity characteristics, six replicate plants, located in the center of the plot, were sampled for strobilus gas exchange traits. Sixteen days after anthesis, ten-day interval repeated measurements began on fully expanded strobili using a portable gas exchange system (CIRAS-2, PP Systems, Haverhill, MA, USA). A PP Systems environmentally controlled conifer branchlet cuvette (Model PLC5 (C)) was used to measure whole strobili. PAR was controlled with a full-spectrum light-emitting diode and temperature by means of Peltier elements fitted with heat sinks and fans (Model PLC5 (C), PP Systems, Haverhill, MA, USA). The measurements were performed at a controlled VPD of 1.5 kPa and temperature of 25 • C. A preliminary experiment indicated A n stability after 10 min per CO 2 change and five minutes per PAR change.
Immediately after gas exchange, five replicate light absorptance samples were recorded per strobilus on random bracts within the strobilus with an SPAD meter and averaged (model 502B, Minolta Inc., Ramsey, NJ, USA). The SPAD values were used to correct apparent quantum yield (φ a ) to φ, as described in Bauerle et al. [37]. For photosynthesis calculations, surface bract area (BA) per hop strobilus was measured and calculated as the total surface area of a cone: BA = πr (r + l), where radius (r) and slant height (l) account for the area of the cylinder base and the cone. (R 2 = 0.968, n = 5; unpublished data).

A n /C i Curve Fitting
The model of Farquhar, von Caemmerer, and Berry [38] was used to estimate the maximum Rubisco carboxylation rate (V cmax ) under light saturation due to the capability of estimating in vivo Rubisco activity. The A n /C i data were analyzed as per the fitting method "fitaci" function of the "plantecophys" package [39] according to Wullschelger [40], where the minimum of any of the three factors Rubisco activity (A nc ), electron transport (A nj ), and inorganic phosphate supply (A np ) can limit CO 2 assimilation, as summarized in von Caemmerer et al. [41] A n = min (A nc , A nj , A np ), The partial pressure of CO 2 in the chloroplast at which photorespiratory CO 2 evolution equals the rate of carboxylation (Γ*; 38.6 umol m −2 s −1 ) at 25 • C and 21% O 2 was as in von Caemmerer et al. [42], assuming an average atmospheric pressure of 847 mbar in Fort Collins, Colorado. The Γ was calculated from the fitted curve.

A n /PAR Curve Fitting
Photosynthesis versus PAR data were fitted to the nonrectangular hyperbola model of Prioul and Chartier [43], as described in Parsons et al. [44] where A max is the light-saturated net photosynthetic rate, φ a is the apparent quantum yield of assimilation, ø is the convexity of the curve, and R d is the respiration rate. The parameter φ a was calculated through linear regression analysis on the initial slope from 20-125 µmol m −2 s −1 to exclude the Kok effect region (≤20 µmol m −2 s −1 ) [45] and prevent φ a underestimation from data in the non-linear region (≥125 µmol m −2 s −1 ) [46]. The light compensation point (Q c ) was estimated from the intersection of the regression line with the x-axis (A n = 0), and R d was measured at the end of the A n /PAR curve. The quantum yield for CO 2 (φCO 2 ) was derived from φ a by correcting φ a for the percentage leaf absorptance of PAR, as described in Bauerle et al. [29]. Equation (3) was fitted separately for the independent A n /PAR curves (Photosyn Assistant, Ver. 1.1.2, Dundee Scientific, Dundee, UK).

Diurnal Strobilus Carbon Balance Estimates
Photosynthetic light response and A n /C i parameters were used to parameterize deterministic strobilus-level models for energy balance [47], stomatal conductance (e.g., [48,49]), and photosynthesis [38] (Table 1). A simulation of carbon gain was performed at light saturation to estimate the impacts of atmospheric elevated CO 2 . To place the strobilus CO 2 responses in the context of strobilus diurnal carbon gain, the photoperiod was set at 15 h, the approximate day length for strobilus physiological functions in Yakima, WA, (46.6021 • N, 120.5059 • W) at the beginning of August (day of year 213). Half-hourly averages of incident PAR, temperature, RH, and wind speed in Yakima, WA, were downloaded from the Washington State University AgWeatherNet site. Atmospheric CO 2 concentrations of 415, 600, 900, 1200, 1500, and 1800 µmol mol −1 were inputted to estimate strobilus carbon gain responses to CO 2 enrichment.
Predicted strobilus carbon gain (C g ) is a direct estimate of carbohydrate biosynthesis: where A n ;light is the total A n during the light period, R;dark is the total respiration during the dark period, and 12 is the molecular mass of C. We summed 30 min diurnal carbon estimates to arrive at net daily C g per strobilus surface area.

Bine Defoliation and Bract Photosynthesis Interruption
To investigate the carbon source for lupulin biosynthesis on the plant scale, six replicates were randomly assigned to either the "defoliation" or "control" group. The control was left to grow normally, and the defoliation group had all leaves removed using scissors at the strobili stigma senescence stage. The strobili stigma senescence stage, described in the comprehensive strobilus developmental stage index of Kavalier et al. [50], is informative because it occurs in advance of biosecratory lupulin production (gland filling) [50]. On the strobilus scale, a photosynthetic inhibitor was used to assess the contribution of bract photosynthesis to lupulin biosynthesis. Paraquat (1,1 -dimethyl-4,4 -bipyridylium), an herbicide absorbed very quickly by leaves, was applied to random bracts at a concentration of 250 g/L via CCT2425 swabs (Chemtronics ® Kennesaw, GA, USA) to inhibit electron transport and CO 2 assimilation. Per strobilus, several random bracts were swabbed with Paraquat from the bract tip proceeding inward toward the strig, covering approximately two thirds of the top surface of an individual bract. Six replicate plants each per defoliation or control group were treated. Strobili were harvested upon maturity and lupulin gland secretions were visually assessed at 40× magnification on Paraquat-treated and untreated bracts per strobilus.

Statistical Analysis
The total sample size for A n /PAR and A n /C i curves was six replicates (n = 6), with one strobilus per six replicate plants. Each strobilus was repeatedly measured at ten-day intervals over the course of four repeated measures (40 days). Each plant was an experimental unit treated as a replicate (n = 6). Two-tailed t-tests were used to analyze the significance between each combination of repeated time measurements. Plant response data were analyzed using SPSS (IBM Analytics, Armonk, NY, USA, www.ibm.com/analytics/ (accessed on 7 November 2022)). Differences between means were considered significant when the p value of the t-value was < 0.05.

Data Availability Statement:
The data presented in this study are available on request from the corresponding author.